Intercropping with sunflower and inoculation with arbuscular mycorrhizal fungi promotes growth of garlic chive in metal-contaminated soil at a WEEE-recycling site.
Identifieur interne : 000700 ( Main/Corpus ); précédent : 000699; suivant : 000701Intercropping with sunflower and inoculation with arbuscular mycorrhizal fungi promotes growth of garlic chive in metal-contaminated soil at a WEEE-recycling site.
Auteurs : Yu Zhang ; Junli Hu ; Jianfeng Bai ; Hua Qin ; Junhua Wang ; Jingwei Wang ; Xiangui LinSource :
- Ecotoxicology and environmental safety [ 1090-2414 ] ; 2019.
English descriptors
- KwdEn :
- Agriculture (methods), Biodegradation, Environmental (MeSH), Biomass (MeSH), Chive (MeSH), Electronic Waste (MeSH), Helianthus (MeSH), Metals, Heavy (analysis), Metals, Heavy (metabolism), Mycorrhizae (MeSH), Phosphorus (metabolism), Plant Roots (chemistry), Plant Roots (growth & development), Plant Shoots (chemistry), Plant Shoots (growth & development), Recycling (MeSH), Soil Pollutants (analysis), Soil Pollutants (metabolism), Waste Disposal Facilities (MeSH).
- MESH :
- chemical , analysis : Metals, Heavy, Soil Pollutants.
- chemical , metabolism : Metals, Heavy, Phosphorus, Soil Pollutants.
- chemistry : Plant Roots, Plant Shoots.
- growth & development : Plant Roots, Plant Shoots.
- methods : Agriculture.
- Biodegradation, Environmental, Biomass, Chive, Electronic Waste, Helianthus, Mycorrhizae, Recycling, Waste Disposal Facilities.
Abstract
Heavy metal (HM) pollution in agricultural soils due to the recycling of waste electrical and electronic equipment (WEEE) has become a serious concern, but most farmers cannot afford the economic losses of fallow land during remediation. Thus, it is imperative to produce low-HM crops while remediating the contaminated soils. A 17-week pot experiment was conducted to investigate the growth and HM (Cd, Cu, Pb, Cr, Zn, and Ni) acquisition of garlic chives (Allium tuberosum Rottl. ex Spreng.) intercropped with sunflower (Helianthus annuus L.) and inoculated with (I+M) or without (I-M) the arbuscular mycorrhizal (AM) fungus Funneliformis caledonium on a severely HM-contaminated soil that was collected from a WEEE-recycling site. Compared with the monoculture control, the I-M treatment significantly (P < 0.05) decreased Cd, Cu, Cr, Zn, and Ni concentrations in the shoots of chives through rhizosphere competition and HM (except Cr) transfer from the root to the shoot of chives, and increased the average shoot fresh weight (i.e., yield) of chives by 794% by alleviating HM toxicity. Compared with the I-M treatment, the I+M treatment significantly increased soil phosphatase activity as well as root mycorrhizal colonization of both sunflower and chives. The I+M treatment had no effect on the tissue P concentration of sunflower but elevated the average dry biomass (shoot plus root) and P acquisition level of sunflower by 179% and 121%, respectively. In addition, the I+M treatment significantly increased the P concentration in the root rather than in the shoot of chives and significantly increased the level of P acquisition by chives, increasing the average yield of chives by 229%. Simultaneously, the I+M treatment significantly increased the level of HM (except Cd) acquisition by sunflower, enhancing the rhizosphere competition by sunflower over chives, and further reducing the transfer of all six HMs from root to shoot in the chives, and inducing significant decreases in chive shoot HM concentrations compared with the monoculture control. Furthermore, the I+M treatment decreased the average total concentrations and increased the average DTPA-extractable concentrations of soil HMs. The results demonstrate the multifunctional role of AM fungi in the intercropping system for both vegetable production and phytoremediation on HM-contaminated soils.
DOI: 10.1016/j.ecoenv.2018.10.046
PubMed: 30366271
Links to Exploration step
pubmed:30366271Le document en format XML
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<affiliation><nlm:affiliation>State Key Laboratory of Soil and Sustainable Agriculture, Institute of Soil Science, Chinese Academy of Sciences, Nanjing 210008, China; Shanghai Collaborative Innovation Centre for WEEE Recycling, WEEE Research Centre of Shanghai Polytechnic University, Shanghai 201209, China.</nlm:affiliation>
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<author><name sortKey="Zhang, Yu" sort="Zhang, Yu" uniqKey="Zhang Y" first="Yu" last="Zhang">Yu Zhang</name>
<affiliation><nlm:affiliation>State Key Laboratory of Soil and Sustainable Agriculture, Institute of Soil Science, Chinese Academy of Sciences, Nanjing 210008, China; Shanghai Collaborative Innovation Centre for WEEE Recycling, WEEE Research Centre of Shanghai Polytechnic University, Shanghai 201209, China.</nlm:affiliation>
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<author><name sortKey="Hu, Junli" sort="Hu, Junli" uniqKey="Hu J" first="Junli" last="Hu">Junli Hu</name>
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<affiliation><nlm:affiliation>Shanghai Collaborative Innovation Centre for WEEE Recycling, WEEE Research Centre of Shanghai Polytechnic University, Shanghai 201209, China.</nlm:affiliation>
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<author><name sortKey="Lin, Xiangui" sort="Lin, Xiangui" uniqKey="Lin X" first="Xiangui" last="Lin">Xiangui Lin</name>
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<term>Chive (MeSH)</term>
<term>Electronic Waste (MeSH)</term>
<term>Helianthus (MeSH)</term>
<term>Metals, Heavy (analysis)</term>
<term>Metals, Heavy (metabolism)</term>
<term>Mycorrhizae (MeSH)</term>
<term>Phosphorus (metabolism)</term>
<term>Plant Roots (chemistry)</term>
<term>Plant Roots (growth & development)</term>
<term>Plant Shoots (chemistry)</term>
<term>Plant Shoots (growth & development)</term>
<term>Recycling (MeSH)</term>
<term>Soil Pollutants (analysis)</term>
<term>Soil Pollutants (metabolism)</term>
<term>Waste Disposal Facilities (MeSH)</term>
</keywords>
<keywords scheme="MESH" type="chemical" qualifier="analysis" xml:lang="en"><term>Metals, Heavy</term>
<term>Soil Pollutants</term>
</keywords>
<keywords scheme="MESH" type="chemical" qualifier="metabolism" xml:lang="en"><term>Metals, Heavy</term>
<term>Phosphorus</term>
<term>Soil Pollutants</term>
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<keywords scheme="MESH" qualifier="chemistry" xml:lang="en"><term>Plant Roots</term>
<term>Plant Shoots</term>
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<term>Chive</term>
<term>Electronic Waste</term>
<term>Helianthus</term>
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<front><div type="abstract" xml:lang="en">Heavy metal (HM) pollution in agricultural soils due to the recycling of waste electrical and electronic equipment (WEEE) has become a serious concern, but most farmers cannot afford the economic losses of fallow land during remediation. Thus, it is imperative to produce low-HM crops while remediating the contaminated soils. A 17-week pot experiment was conducted to investigate the growth and HM (Cd, Cu, Pb, Cr, Zn, and Ni) acquisition of garlic chives (Allium tuberosum Rottl. ex Spreng.) intercropped with sunflower (Helianthus annuus L.) and inoculated with (I<sub>+M</sub>
) or without (I<sub>-M</sub>
) the arbuscular mycorrhizal (AM) fungus Funneliformis caledonium on a severely HM-contaminated soil that was collected from a WEEE-recycling site. Compared with the monoculture control, the I<sub>-M</sub>
treatment significantly (P < 0.05) decreased Cd, Cu, Cr, Zn, and Ni concentrations in the shoots of chives through rhizosphere competition and HM (except Cr) transfer from the root to the shoot of chives, and increased the average shoot fresh weight (i.e., yield) of chives by 794% by alleviating HM toxicity. Compared with the I<sub>-M</sub>
treatment<sub>,</sub>
the I<sub>+M</sub>
treatment significantly increased soil phosphatase activity as well as root mycorrhizal colonization of both sunflower and chives. The I<sub>+M</sub>
treatment had no effect on the tissue P concentration of sunflower but elevated the average dry biomass (shoot plus root) and P acquisition level of sunflower by 179% and 121%, respectively. In addition, the I<sub>+M</sub>
treatment significantly increased the P concentration in the root rather than in the shoot of chives and significantly increased the level of P acquisition by chives, increasing the average yield of chives by 229%. Simultaneously, the I<sub>+M</sub>
treatment significantly increased the level of HM (except Cd) acquisition by sunflower, enhancing the rhizosphere competition by sunflower over chives, and further reducing the transfer of all six HMs from root to shoot in the chives, and inducing significant decreases in chive shoot HM concentrations compared with the monoculture control. Furthermore, the I<sub>+M</sub>
treatment decreased the average total concentrations and increased the average DTPA-extractable concentrations of soil HMs. The results demonstrate the multifunctional role of AM fungi in the intercropping system for both vegetable production and phytoremediation on HM-contaminated soils.</div>
</front>
</TEI>
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<Title>Ecotoxicology and environmental safety</Title>
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<ArticleTitle>Intercropping with sunflower and inoculation with arbuscular mycorrhizal fungi promotes growth of garlic chive in metal-contaminated soil at a WEEE-recycling site.</ArticleTitle>
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<Abstract><AbstractText>Heavy metal (HM) pollution in agricultural soils due to the recycling of waste electrical and electronic equipment (WEEE) has become a serious concern, but most farmers cannot afford the economic losses of fallow land during remediation. Thus, it is imperative to produce low-HM crops while remediating the contaminated soils. A 17-week pot experiment was conducted to investigate the growth and HM (Cd, Cu, Pb, Cr, Zn, and Ni) acquisition of garlic chives (Allium tuberosum Rottl. ex Spreng.) intercropped with sunflower (Helianthus annuus L.) and inoculated with (I<sub>+M</sub>
) or without (I<sub>-M</sub>
) the arbuscular mycorrhizal (AM) fungus Funneliformis caledonium on a severely HM-contaminated soil that was collected from a WEEE-recycling site. Compared with the monoculture control, the I<sub>-M</sub>
treatment significantly (P < 0.05) decreased Cd, Cu, Cr, Zn, and Ni concentrations in the shoots of chives through rhizosphere competition and HM (except Cr) transfer from the root to the shoot of chives, and increased the average shoot fresh weight (i.e., yield) of chives by 794% by alleviating HM toxicity. Compared with the I<sub>-M</sub>
treatment<sub>,</sub>
the I<sub>+M</sub>
treatment significantly increased soil phosphatase activity as well as root mycorrhizal colonization of both sunflower and chives. The I<sub>+M</sub>
treatment had no effect on the tissue P concentration of sunflower but elevated the average dry biomass (shoot plus root) and P acquisition level of sunflower by 179% and 121%, respectively. In addition, the I<sub>+M</sub>
treatment significantly increased the P concentration in the root rather than in the shoot of chives and significantly increased the level of P acquisition by chives, increasing the average yield of chives by 229%. Simultaneously, the I<sub>+M</sub>
treatment significantly increased the level of HM (except Cd) acquisition by sunflower, enhancing the rhizosphere competition by sunflower over chives, and further reducing the transfer of all six HMs from root to shoot in the chives, and inducing significant decreases in chive shoot HM concentrations compared with the monoculture control. Furthermore, the I<sub>+M</sub>
treatment decreased the average total concentrations and increased the average DTPA-extractable concentrations of soil HMs. The results demonstrate the multifunctional role of AM fungi in the intercropping system for both vegetable production and phytoremediation on HM-contaminated soils.</AbstractText>
<CopyrightInformation>Copyright © 2018 Elsevier Inc. All rights reserved.</CopyrightInformation>
</Abstract>
<AuthorList CompleteYN="Y"><Author ValidYN="Y"><LastName>Zhang</LastName>
<ForeName>Yu</ForeName>
<Initials>Y</Initials>
<AffiliationInfo><Affiliation>State Key Laboratory of Soil and Sustainable Agriculture, Institute of Soil Science, Chinese Academy of Sciences, Nanjing 210008, China; Shanghai Collaborative Innovation Centre for WEEE Recycling, WEEE Research Centre of Shanghai Polytechnic University, Shanghai 201209, China.</Affiliation>
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<AffiliationInfo><Affiliation>State Key Laboratory of Soil and Sustainable Agriculture, Institute of Soil Science, Chinese Academy of Sciences, Nanjing 210008, China; University of Chinese Academy of Sciences, Beijing 100049, China. Electronic address: jlhu@issas.ac.cn.</Affiliation>
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</AffiliationInfo>
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<Initials>H</Initials>
<AffiliationInfo><Affiliation>Key Laboratory of Soil Contamination Bioremediation of Zhejiang Province, School of Environmental and Resource Sciences, Zhejiang A & F University, Hanghou 311300, China.</Affiliation>
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<AffiliationInfo><Affiliation>State Key Laboratory of Soil and Sustainable Agriculture, Institute of Soil Science, Chinese Academy of Sciences, Nanjing 210008, China.</Affiliation>
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<Author ValidYN="Y"><LastName>Wang</LastName>
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<Initials>J</Initials>
<AffiliationInfo><Affiliation>Shanghai Collaborative Innovation Centre for WEEE Recycling, WEEE Research Centre of Shanghai Polytechnic University, Shanghai 201209, China.</Affiliation>
</AffiliationInfo>
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<Author ValidYN="Y"><LastName>Lin</LastName>
<ForeName>Xiangui</ForeName>
<Initials>X</Initials>
<AffiliationInfo><Affiliation>State Key Laboratory of Soil and Sustainable Agriculture, Institute of Soil Science, Chinese Academy of Sciences, Nanjing 210008, China.</Affiliation>
</AffiliationInfo>
</Author>
</AuthorList>
<Language>eng</Language>
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</PublicationTypeList>
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<Month>10</Month>
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<QualifierName UI="Q000378" MajorTopicYN="Y">metabolism</QualifierName>
</MeshHeading>
<MeshHeading><DescriptorName UI="D038821" MajorTopicYN="Y">Mycorrhizae</DescriptorName>
</MeshHeading>
<MeshHeading><DescriptorName UI="D010758" MajorTopicYN="N">Phosphorus</DescriptorName>
<QualifierName UI="Q000378" MajorTopicYN="N">metabolism</QualifierName>
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<MeshHeading><DescriptorName UI="D018517" MajorTopicYN="N">Plant Roots</DescriptorName>
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<MeshHeading><DescriptorName UI="D059027" MajorTopicYN="N">Recycling</DescriptorName>
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<Keyword MajorTopicYN="N">Phosphatase</Keyword>
<Keyword MajorTopicYN="N">Phytoremediation</Keyword>
<Keyword MajorTopicYN="N">Quality safety of agricultural products</Keyword>
<Keyword MajorTopicYN="N">Vegetable</Keyword>
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<Month>10</Month>
<Day>05</Day>
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